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J Comp Physiol B (2008) 178:997–1005
DOI 10.1007/s00360-008-0290-8
O R I G I N A L A R T I CL E
Variation in stress and innate immunity in the tree lizard
(Urosaurus ornatus) across an urban–rural gradient
Susannah S. French · H. Bobby Fokidis ·
Michael C. Moore
Received: 2 April 2008 / Revised: 16 June 2008 / Accepted: 19 June 2008 / Published online: 2 July 2008
© Springer-Verlag 2008
Abstract The urban environment presents new and diVerent challenges to wildlife, but also potential opportunities
depending on the species. As urban encroachment onto
native habitats continues, understanding the impact of this
expansion on native species is vital to conservation. A key
physiological indicator of environmental disturbance is the
vertebrate stress response, involving increases in circulating glucocorticoids (i.e. corticosterone), which exert
inXuence on numerous physiological parameters including
energy storage, reproduction, and immunity. We examined
how urbanization in Phoenix, Arizona inXuences corticosterone levels, blood parasitism, and innate immunity in
populations of tree lizards (Urosaurus ornatus) to determine whether urbanization may be detrimental or beneWcial
to this species. Both baseline and stress-induced corticosterone concentrations were signiWcantly lower in urban lizards relative to the rural ones, however, the magnitude of
the increase in corticosterone with stress did not diVer
across populations. Urban lizards also had a lower ratio of
heterophils to lymphocytes, but elevated overall leukocyte
count, as compared to lizards from the natural site. Urban
and rural lizards did not diVer in their prevalence of the
blood parasite, Plasmodium mexicanum. Taken together,
these results suggest that urban tree lizards may have
Communicated by H.V. Carey.
S. S. French (&)
Center for the Integrative Study of Animal Behavior
and Department of Biology, Indiana University,
1001 E. 3rd Street, Bloomington, IN 47405, USA
e-mail: [email protected]
H. B. Fokidis · M. C. Moore
Organismal, Integrative, and Systems Biology,
School of Life Sciences, Arizona State University,
College and University Dr., Tempe, AZ 85287-4501, USA
suppressed overall corticosterone concentrations possibly
from down-regulation as a result of frequent exposure to
stressors, or increased access to urban resources. Also, urban
lizards may have bolstered immunocompetence possibly
from increased immune challenges, such as wounding, in the
urban environment, or from greater energetic reserves being
available as a result of access to urban resources.
Keywords Disturbance · Corticosterone · Leukocytes ·
Urbanization · Parasites
Introduction
As human-dominated landscapes encroach on native habitats, the ability of animals to adapt to these novel environments will become an increasingly important factor for
their long-term persistence. In cities animals contend with
repeated, yet highly variable anthropogenic disturbances, as
well as drastic changes to their native habitats (Shochat
et al. 2006). Although urbanization is usually regarded as
detrimental to animal populations, recent research into
urban ecology has demonstrated organismal responses as
variable and species speciWc (Hostetler 1999; Hostetler and
Knowles-Yanez 2003). Cities present novel “stressors” to
wildlife including: human disturbance (Fernandez-Juricic
2002), vehicle traYc (Bautista et al. 2004), non-native predators (Koenig et al. 2002; Woods et al. 2003; Baker et al.
2005), exposure to pollutants (Eens et al. 1999; Burger
et al. 2004), and warmer ambient temperatures (McLean
et al. 2005). Despite these factors some species persist in
cities which may provide advantages to species equipped to
exploit them (Ficetola et al. 2007; Bonier et al. 2007b).
These beneWts may include: abundant exotic and anthropogenic food resources (Parris and Hazell 2005; Anderies
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et al. 2007), refuge from solar exposure in the form of ornamental trees (Braman et al. 2000), and year-round water
resources (Fokidis et al. 2008). The latter may be especially
important in arid regions, where water is the predominant
factor inXuencing the timing of life-history events in all
desert Xora and fauna (Beck et al. 1973; Giuliano et al.
1995; Vleck 1984). Urban water sources may also harbor
parasite-transmitting vectors (Fokidis et al. 2008) which
have aquatic life-stages (Marquardt et al. 2000). Parasitic
infection can negatively inXuence the overall health of
urban wildlife, and may interfere with colonization success
(Garamszegi et al. 2007). The ability of a species to avoid
the costs and reap the beneWts of city environments may be
an important determinant of the relative success of acclimatization to urbanization.
Although studies have documented demographic changes
in wildlife resulting from urban development, only recently
have the physiological consequences of urbanization been
examined. In vertebrates, environmental stressors are usually detected as increases in circulating glucocorticoids,
such as corticosterone (CORT) result from the activation of
the hypothalamic-pituitary-adrenal (HPA) axis (Sapolsky
et al. 2000). The HPA axis functions to mobilize nutrient
stores, and modify behaviors during stressful situations and
activation is adaptive in the short term, but detrimental if
long term (Sapolsky et al. 2000). The ability to modulate
HPA functioning allows normal life-history processes to
continue despite of environmental change (WingWeld et al.
1998; Astheimer et al. 1995; Boonstra et al. 2001). To date,
all studies of urbanization and HPA functioning in wildlife
have been done on birds. These studies have demonstrated
population-level variation in stress-responsiveness associated with urbanization, with urban birds either showing
suppressed (Partecke et al. 2006) or increased CORT production (Schoech et al. 2004; H. B. Fokidis et al., in review)
in response to an acute stressor compared to rural birds.
Thus, urban-associated variation in stress-responsiveness is
species-speciWc H. B. Fokidis et al., in review) and likely
sex-speciWc (Bonier et al. 2007a).
Tree lizards (Urosaurus ornatus) are a small phrynosomatid lizard species found throughout the southwestern
US and Northern Mexico and are abundant on boulders,
trees, and shrubs throughout urban localities in the Sonoran
Desert. This wide distribution encompassing numerous
habitat types make tree lizards a useful model for examining the physiological consequences of urbanization. Additionally, the stress physiology, reproduction, behavior, and
seasonal hormone proWles of this species have been extensively studied in both captive and wild populations (Moore
et al. 1998; Moore et al. 1991; Thompson and Moore 1992;
Woodley and Moore 2002). In tree lizards increases in
CORT resulting from restraint stress depresses wound healing, a measure of innate immunity (French et al. 2006,
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J Comp Physiol B (2008) 178:997–1005
2007c). During energy-limiting conditions, wild female
tree lizards trade oV investment into immune function with
that into reproduction (French et al. 2007a; French and
Moore 2008). This highlights the energetic cost of maintaining immunity and thus potentially “stressful” components of the urban environment may inXuence immune
function, which may be particularly important during energetically taxing life-history stages.
We examined stress-responsiveness and innate immune
function in tree lizards living within and around Phoenix,
AZ. SpeciWcally, we attempt to diVerentiate between the
two hypotheses. The Wrst hypothesis suggests that exposure
to acute urban stressors and the presence of parasite-transmitting vectors in urban water resources will result in urban
lizards having higher baseline CORT levels, impaired
stress-responsiveness, increased blood parasitism, and lowered immune capacity (changes in number and distribution
of leucocytes). An alternate hypothesis proposes that tree
lizards in urban areas will acclimatize to repetitive and
benign urban “stressors” and increased access to urban food
and water resources may act to lower baseline CORT levels. Alternatively, studies in birds show that prolonged elevations in CORT levels that are associated with chronic
stress can act to down-regulated HPA functioning resulting
in decreased baseline CORT levels (Cyr et al. 2007; Rich
and Romero 2005). In addition, acclimatization to benign
urban stressors may enable urban lizards to maintain a bolstered stress response. In turn, urban lizards may show a
strengthened immune capacity and lower levels of blood
parasitism compared to rural conspeciWcs. This study is the
Wrst to examine the physiological consequences of urbanization in a non-avian species and provides preliminary
insight into how endocrine and immunological mechanisms
may interact to inXuence the colonization of novel habitats
by native species.
Methods
Field sampling and study sites
Male and female tree lizards were sampled from 18 to 28
April 2007 (between 1000 and 1400 h) at three sites located
within and around Phoenix, AZ. Two sites were centrally
located in the Phoenix metropolitan area in close proximity
to one another. The Wrst was an urban site (urban, U: 33°
26.12 N, 111° 55.83 W) which consisted of residential
housing developments constructed in 1955 and contained
both xeric and mesic (i.e. grass) landscaping. The second
site (semi-natural, SN: 33° 26.19 N, 111° 55.87 W) was a
protected desert remnant (Papago Park) located about 1 km
west of the urban site. Here the habitat consists of a heterogenous matrix of upland and lowland native Sonoran
J Comp Physiol B (2008) 178:997–1005
Desert vegetation, as well as both native and ornamental
riparian plant species. We also sampled an undeveloped
rural site located in the McDowell Mountain Sonoran
Reserve (natural, N: 33° 41.54 N, 111° 47.26 W) located
near the Northern periphery of Phoenix, about 21 km from
the other two sites. This site is composed of large tracts of
typical native upland Sonoran Desert region Xora.
All animals included in the study were sexually mature,
reproductive adults. Lizards were captured by noosing and a
blood sample was taken, by rupturing the orbital sinus with
a heparinized capillary tube, within 3 min of initial sighting.
Upon capture lizards were bled immediately and no longer
than 30 sec was taken to obtain a blood sample. Lizards
were then placed individually in opaque cloth bags for
10 min, after which a second blood sample was taken (hereafter “stress-induced”). This enabled us to assess change in
CORT concentrations in response to the stress of capture
and handling. Past studies in tree lizards showed a signiWcant stress-related increase in CORT levels by 10 min with a
maximum increase attained at approximately 60 min
(Moore et al. 1991). Plotting the CORT trajectory, we can
estimate the magnitude of the overall increase based on the
10-min sample (Moore et al. 1991). Thus, we examined two
measures; the concentration of CORT after 10 min of capture/handling stress, and the rate of increase in CORT levels
within 10 min with respect to baseline levels (i.e. magnitude
of change in CORT). Blood was stored on ice until transported back to the laboratory. Thin blood smears were made
in the Weld on glass microscope slides using about 5 l of
the initial blood sample (Bennett 1970; Walberg 2001; Fokidis et al. 2008). Smears were air-dried at ambient temperature and stored until Wxation. We assessed reproductive
condition of females by manually palpating the abdomen for
the number and Wrmness of follicles/eggs, whereas all males
were in reproductive condition during sampling (French and
Moore 2008). Males are known to be in breeding condition
during the chosen sampling period based on previous studies
which assessed testes size (French and Moore 2008). We
also recorded the presence of scars and injuries, including
caudal autotomy (i.e. tail breaks), which are common in
many lizard species, and evidence of past stressor (Table 1).
Lastly, we recorded snout-vent length (SVL) deWned as the
length from the tip of the animal’s snout to its cloacal vent.
All handling and procedures were approved by Arizona
State University’s Institutional Animal Care and Use Committee, protocol # 03-678R.
Plasma samples and radioimmunoassay
In the laboratory plasma was separated from the blood via
centrifugation (30 min at 2,500 rpm) and stored at ¡20°C
until assayed. Plasma samples were assayed for CORT in
duplicate and within a single radioimmunoassay previously
999
Table 1 Mean snout-vent length (SVL) § 1 standard error and
prevalence of plasmodium (percentage infected with plasmodium), for
female and male tree lizards (Urosaurus ornatus) sampled at three sites
(see text) across an urban–rural gradient
Site
Sex
n
SVL (mm)
Plasmodium
prevalence (%)
U
Female
9
49.89 § 1.53a
22
33.3a
Male
7
51.79 § 1.52
14
28.6a
Female
6
43.25 § 1.36
33
0
Male
9
52.22 § 1.25
11
0
Female
5
43.60 § 0.29
20
0
Male
5
47.2 § 2.44
0
0
SN
N
% Wounded
animals
n indicates sample size
a
SigniWcant diVerences from other sites at = 0.05
described in (Moore 1986). In brief, samples were extracted
using 30% ethyl acetate/isooctane extractions. The 30%
phase was separated, dried, and resuspended in 90% ethanol. Samples were then washed with hexane to remove
excess lipids and were resuspended in PBS buVer. Duplicate aliquots of these samples were then assayed for CORT.
The intra-assay coeYcient of variation was 9% for CORT.
Blood smears and analysis
Blood smears were Wxed for 10 min in absolute methanol
within 3 days of collection and subsequently Giemsastained (Bennett 1970). Stained smears were then dehydrated for one week under partial vacuum. Stained slides
were then cleared using xylene, cover-slipped, and sealed
using Cytoseal 60 (VWR, San Francisco, CA) to facilitate
long-term storage. Parasite prevalence, the percentage of
infected individuals in a population (Bush et al. 1997) was
determined by surveying blood smears at 250£ magniWcation for 10 min and then at 400£ magniWcation for 5 min
using an Olympus BX60 light microscope (Olympus Optical Co., Tokyo, Japan).
To assess innate immunity we examined the ratio of
heterophil leukocytes to lymphocytes (H:L). This measure is
often used as an indicator of chronically elevated glucocorticoids resulting from “stressful” stimuli (Gross and Siegel
1986; Vleck et al. 2000; Bonier et al. 2007a), which can suppress lymphocyte numbers, in whole blood (Harmon 1998).
We examined randomly selected and non-overlapping microscope Welds in each smear under oil immersion (1,000£
magniWcation) and counted leukocytes until a total of 100
white blood cells was reached (Fokidis et al. 2008). We identiWed eosinophils, basophils, and monocytes, using the criteria of (Campbell 1996); however; only heterophils and
lymphocytes as a ratio were analyzed statistically. All slides
were examined by a single observer (H.B.F.) without knowledge of locality, sex, or date that the samples were collected.
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Another measure of innate immunity is the total number
of circulating leukocytes, usually expressed as a total leukocyte count (TLC) (Godfrey et al. 1987; Gering and
Atkinson 2004). To obtain the TLC, 25 randomly selected
non-overlapping microscope Welds containing non-overlapping single cell layers were digitized at 400£ magniWcation.
Image-Pro analysis software (v. 4.1, Media Cybernetics,
Silver Springs, MD, USA) was then used to identify 10,000
erythrocytes per slide, which is the minimum recommended
for accurate assessment of TLC (Gering and Atkinson
2004). Erythrocytes were identiWed based on morphological characteristics of their nucleus (aspect ratio, length,
width, perimeter, roundness, relative brightness, and color)
and were included in the counts if their entire nucleus was
visible on the digitized image. Leukocytes as well as
infected erythrocytes seen on these digitized images were
manually counted and expressed as the number of leukocytes per 10,000 non-infected erythrocytes.
Statistical analyses
Initially, t tests were performed to assess sex-biased diVerences for all continuous variables to determine whether or
not sexes could be pooled for subsequent analysis. Hormonal and hematology data were log-transformed to satisfy
the assumptions of normality and equal variances. Repeated
measures analysis of variance (ANOVA) was used to
assess site diVerences in circulating hormone concentrations. These data violated assumptions of sphericity and
thus were Greenhouse–Geiser corrected, which conservatively adjusts the degrees of freedom. Separate one-way
ANOVAs, with an level adjusted using Bonferroni, were
used to assess site diVerences in concentration and magnitude of changes in CORT, hematology and SVL. Tukey–
Kramer honestly signiWcant diVerence (HSD) corrected
post-hoc comparisons allowed us to discern diVerences
between sites. Parasite prevalence was compared with hierarchical log-linear analysis, which tests for associations
between categorical variables in a manner similar to
ANOVA (Fokidis et al. 2008). The signiWcance level for all
statistical tests was = 0.05, unless otherwise stated. Data
are presented as means § 1 standard error (SE). All statistical analyses were performed using JMP.IN (v. 5.1, SAS
Institute Inc., Cary, NC, USA) and SPSS (v. 13, SPSS Inc.,
Chicago, IL, USA).
Results
Snout-vent length
Body size is usually a sexually dimorphic characteristic in
tree lizards (French and Moore 2008), and therefore the
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J Comp Physiol B (2008) 178:997–1005
sexes were analyzed separately for SVL. There was a signiWcant diVerence in SVL among the diVerent sites for
females (F2,19 = 7.58, P < 0.01) but not males (F2,20 = 2.45,
P = 0.11). The females at site U were signiWcantly larger
than females from the other sites (SN, N), according to post
hoc comparisons (Table 1).
Corticosterone data
There was no signiWcant sex diVerence in baseline
(t = 0.45, df = 1, P = 0.65) or stress-induced increase
(t = 0.51, df = 1, P = 0.61) in CORT concentrations, and
therefore hormone data were pooled between the sexes. As
predicted there were signiWcant diVerences in baseline
CORT concentrations (F2,36 = 5.54, P < 0.01; Fig. 1a)
among the sites, with higher circulating concentrations at
the N site, relative to the other sites (SN, U). However,
there was no diVerence in the change in CORT concentration over time (F2,36 = 0.25, P = 0.78; Fig. 1b) among sites.
This was also reXected by no signiWcant diVerence in the
magnitude of change in CORT concentrations among the
populations (F2,38 = 2.58, P = 0.089; Fig. 1b), although
there was a trend for the N population having a greater
change than the U and SN sites. A similar result was
attained using the percentage increase above baseline
CORT levels (F2,38 = 0.12, P = 0.88). Regarding stressinduced concentrations of CORT, the N animals > the U
site lizards > SN animals.
Blood parasites
Only a single blood parasite, Plasmodium mexicanum was
detected at relatively low intensity (6–14 infected cells per
10,000 erythrocytes) during the study. This blood parasite
only infected erythrocytes and was present in 8 of the 41
individuals (19.5% total). Parasite prevalence did not diVer
between sexes (X2 = 0.98, df = 2, P = 0.53; Table 1) or
across sites (X2 = 0.47, df = 3, P = 0.82; Table 1). Infected
lizards did not diVer in SVL from non-infected lizards
(t = 0.83, df = 1, P = 0.49).
Leukocyte counts
There was no diVerence in H:L (t = 0.182, df = 1,
P = 0.857) or TLC (t = 0.169, df = 1, P = 0.866) between
the sexes and thus data were pooled for comparison across
sampling sites. Lizards sampled from the N site had a
greater H:L ratio compared to lizards from either SN or U
sites (F2,38 = 30.91, P < 0.01; Fig. 2a). However, H:L ratio
did not diVer between the SN and U sites (P > 0.9). Lizards
from the N site also had a lower TLC compared to both the
SN or U sites (F2,38 = 9.06, P = 0.006; Fig. 2b) but, lizards
again did not diVer with respect to TLC between these sites
J Comp Physiol B (2008) 178:997–1005
35
Corticosterone (ng/ml)
30
a
Baseline
Stress
25
ab
20
b
15
A
10
B
B
5
0
U
SN
N
a
1.4
Heterophil to Lymphocyte Ratio
a
1001
1.0
0.8
B
0.4
0.2
SN
N
Site
b
25
B
0.6
U
160
A
20
140
Total Leucocyte Count
Corticosterone increase (ng/ml)
A
0.0
Site
b
1.2
15
10
5
120
A
100
B
80
60
40
20
0
U
SN
N
Site
Fig. 1 a Circulating concentrations of corticosterone in tree lizards
(Urosaurus ornatus) before and after handling stress at the urban (U),
semi-natural (SN), and natural (N) sites. Upper case letters denote signiWcant diVerences of baseline levels and lower case letters denote signiWcant diVerences of stress-induced levels of corticosterone among
the diVerent sites ( = 0.05 level). Additionally, stress-induced CORT
concentrations were signiWcantly greater relative to baseline CORT
concentrations for all sites ( = 0.05 level). b The magnitude of the
change in corticosterone, at three sites sampled across the urban–rural
gradient of Phoenix, AZ. (Note, a similar result was found using
percentage increase above baseline.). Error bars represent 1 standard
error
(P = 0.308). Neither, TLC nor H:L ratio were correlated to
SVL (TLC: r = 0.095, N = 41, P = 0.553; H:L ratio:
r = ¡0.282, N = 41, P = 0.074). Infected lizards did not
diVer in H:L ratio or TLC from non-infected lizards (H:L
ratio: t = 0.71, P = 0.83; TLC: t = 1.03, P = 0.091;).
Discussion
The stress of city living in the tree lizard
This study is the Wrst to investigate how physiology can
vary with respect to urbanization in a reptile species. Over-
0
U
SN
N
Site
Fig. 2 a The ratio of heterophil to lymphocyte (H:L) white blood cells
at the urban (U), semi-natural (SN), and natural (N) sites, and b the total leukocyte count (TLC), expressed number of leukocytes per 10,000
red blood cells, for tree lizards (Urosaurus ornatus) sampled at three
sites across the urban–rural gradient of Phoenix, AZ. Error bars represent 1 standard error. Letters denote signiWcant diVerences among
groups at the = 0.05 level
all, baseline and stress-induced CORT concentrations were
elevated in lizards from the natural site, as compared to
counterparts from urban and semi-natural locations. However, there was no diVerence in magnitude of CORT
increase among the populations. This decrease in baseline
CORT in urban and semi-natural lizards supports the
hypothesis that urban lizards either: (1) acclimatized to
repeated stressors in anthropogenically modiWed habitats,
(2) lower overall “stress” as a function of increased availability of food/water resources in the U and SN sites, or (3)
increased chronic activation of the HPA axis, possibly
resulting from higher predation in urban areas. However,
based on the data collected in this study we are unable to
distinguish between these potential underlying causes for
the observed variation in CORT in tree lizards. All scenarios
would manifest as a decrease in overall circulating CORT
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1002
concentrations. This type of response may be adaptive as
chronic elevations in CORT are known to be detrimental to
the health and Wtness of many organisms (Dhabhar and
McEwen 1999; Moore and Jessop 2003). However, we did
not observe any modulation of the stress response in tree
lizards across an urban–natural comparison, which has been
found in many avian studies. Many species modulate their
stress response by decreasing HPA activity in response to
repeated stressors, seasonally, or during energetically
demanding life-history events such as reproduction
(Romero et al. 2008; Wang et al. 2006; Boonstra 2004;
Wada and Shimizu 2004). We sampled lizards only during
the spring and conceivably modulation of the stress
response may occur during other seasons or life-history
stages.
Several diVerent potential stressors for tree lizards exist
in urban habitat as compared to rural areas, including
increased predation risk from nonnative species (Woods
et al. 2003; Baker et al. 2005). In our study, about 30% of
the animals sampled at the U site had a regenerated tail or a
scar of some type, whereas none of the animals sampled at
the other sites had any noticeable scars or injuries. This
suggests increased predation risks in the urban environment, possibly from the numerous domestic cats (Felis silvestris catus) in the area. Domestic cats are known to
predate heavily on lizards in cities (Koenig et al. 2002; Gillies and Clout 2003). These wounds could result in
increased CORT in urban lizards, and a blunted CORT
response by urban lizards may mediate shifts in allocation
of energy to various processes, including wound healing,
which are known to limit resources available to other
important physiological processes such as reproduction
(French et al. 2007b). This is consistent with our observation that U lizards have lower CORT levels than counterparts from the SN or N sites. Decreased CORT levels in
urban lizards may also result from lowered predation from
natural enemies, such as snakes which occur at lower densities in urban environments (Fearn et al. 2001; Reed and
Shine 2002). This is consistent with the “predator-release”
hypothesis, which suggests that urban areas may provide
refuges for species where population dynamics are heavily
impacted by predation pressure from native animals
(Sorace 2002; Jokimaki et al. 2005). However, increased
predation from non-native urban species must also be considered in the context of the predator-release hypothesis,
and may explain lowered baseline CORT levels in the U
site lizards. Similarly, overall lizard diversity decreases in
urban areas (Germaine and Wakeling 2001) and this may
lower competition from native lizard species. These factors
may also act to lower baseline CORT levels in urban populations of tree lizards.
Tree lizards sampled from our natural site had higher
baseline CORT levels than those from either of the modi-
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J Comp Physiol B (2008) 178:997–1005
Wed habitats. Variation in CORT levels between our populations may result from factors unrelated to urbanization.
Individual variation in baseline CORT may be inXuenced
by both past and present conditions in the environment
(Landys et al. 2006; Romero and Reed 2008). Population
diVerences in baseline CORT have been reported in this
species (M.C. Moore, personal observation) and may be
related to variation associated with reproductive state (Wilson and WingWeld 1992; Moore and Mason 2001; Jessop
et al. 2004) or diel patterns of CORT release (Romero and
Remage-Healey 2000; Rodriguez et al. 2001). We sampled
only adult lizards that were in active reproductive condition
and all captures were made within a 10 day period from
1,000 to 1,400 h in an eVort to minimize temporal variation
in CORT. During this 10 day sampling period, the daily
mean air temperature ranged from 21 to 27°C (daily max.:
26–35°C; daily min.: 8–15°C) and all days were characterized as having low cloud cover with little or no wind,
and thus diVerences in weather likely do not account for the
variation in baseline CORT observed between our sites.
The predominant diVerences among our three sampling
sites were the degree of anthropogenic development and
overall habitat cover (N and SN sites have signiWcantly
greater amount of cover than the U site) and these factors
likely inXuence, at least in part, baseline CORT levels (see
Methods for site description). This study is a preliminary
examination and future studies should incorporate more
sites and test speciWc components of urbanization that may
inXuence baseline CORT levels.
Immunocompetence and the urban environment
Compatible with other studies in reptiles (Aguirre et al.
1995; Morici et al. 1997; Cartledge et al. 2005), we
observed an increase in the ratio of heterophils to lymphocytes (H:L) that was consistent with population diVerences
in baseline CORT. Saad and Elridi (1988) report that
CORT acts to lyse lymphocytes in the lizard Chalcides
ocellatus, resulting in depressed overall number of lymphocytes. Similarly, lymphocyte activity was highest in the turtle Mauremys caspica during periods of the year when
steroids, including CORT were at lowest concentrations
(Munoz et al. 2000). Decreases in baseline CORT in the
tree lizards from the U and SN sites may increase lymphocytes, which are involved in speciWc responses to foreign
antigens and ultimately strengthen immune response to
infection. The urban and semi-natural lizards also had
increased total numbers of leukocytes (i.e. TLC). These lizards may be in better overall condition enabling them to
maintain a high reserve of leukocytes in preparation to Wght
potential infections. The observed condition-dependence of
leukocyte numbers may potentially be mediated through
concentrations in CORT.
J Comp Physiol B (2008) 178:997–1005
Another factor that can inXuence the proportions and
total numbers of leukocytes in peripheral blood is whether
the organism is combating a current infection. We observed
only a single blood parasite species, P. mexicanum in our
study, however, its prevalence did not vary with respect to
site and infection was not associated with H:L ratio, TLC or
SVL and was present at low intensity in all infected individuals. These Wndings suggest that the occurrence of vectors for P. mexicanum, such as the sandXies Lutzomyia
vexator and L. stewarti, (Schall and Smith 2006) do not
vary across the urban–rural gradient studied, despite diVerences in the amount of open-standing water between habitats. Additionally, the low intensity of parasitic infection in
our samples may be due to other factors, such as the ability
of the immune system to eradicate or clear parasites from
circulation. The clearance of parasites from circulation may
be mediated by CORT (Hanley and Stamps 2002; Dunlap
and Schall 1995). Infection with blood parasites is typically
associated with decreases in H:L ratio and overall increases
in TLC, because of lymphocyte proliferation (Bonier et al.
2007a). The lack of a relationship between SVL and infection with P. mexicanum in the present study suggests that
parasitism has minimal eVects on tree lizard health, which
are not suYcient to retard growth. Notably, we were unable
to determine how long individuals had been infected and
whether infections were new or the result of relapse in
existing infection, perhaps in response to CORT. Little is
understood concerning the relationship between habitat
(natural or modiWed), parasitism, and immune function,
particularly in arid regions. Future research may allow us to
elucidate patterns, processes, and mechanisms that dictate
long-term responses of species to modiWed habitats.
Future directions in urban physiology
An individual’s ability to respond to environmental perturbations greatly inXuences its short-term survival and ultimate acclimatization to changing environments. Moreover,
glucocorticoids that are involved in the mediation of the
stress response, often have permissive roles in regulating
reproduction, metabolism, and resource distribution. Thus,
it is critical to understand not only how organisms cope
with environmental stressors, but also how diVerent environments aVect the stress response. This preliminary study
examined a single species, yet it is likely that the environmental eVects of the urban landscape on physiology vary
depending on taxa. Furthermore, the fact that tree lizards
readily persist under certain contexts in the urban landscape
make them a useful model for comparison with other
species less tolerant to urbanization such as Urosaurus graciosus or Sceloporus occidentalis. Comparative studies
enable us to elucidate how pre-existing characteristics of
species may enable their successful colonization of novel
1003
environments such as cities. Future studies should examine
multiple cities, particularly ones from diVerent regions containing diVerent habitats. Future studies could also include
additional measures of immunity, as diVerent components
of the immune system can vary in their response to the
eVects of urbanization. A greater understanding of the
physiological implications of urbanization may enable us to
mitigate the impact of growing cities on wildlife.
Acknowledgments We would like to thank Nataliya Emmert for
help with Weld work, Pierre Deviche for use of his light microscope,
and Jon Davis for use of his backyard and alleyway. We would also
like to thank PRG at ASU for critical feedback on this article.
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